University:
California State University, Northridge
Course:
EOH 466B/L | Evaluating the Occupational Environment and Lab
Academic year:

2008
Views:

340

Pages:

27
Author:

bolisse66m

Sampling for Gases and Vapors Gases and Vapors • Gases: don't exist in liquid state at STP – e.g.: nitrous oxides, ozone, carbon monoxide • Vapors: may exist in liquid state at STP – e.g.: toluene, benzene, other solvents; mercury • Distinction moot unless liquid is sprayed. 1 Methods of Sampling • Grab sampling – Evacuated flask: heavy walls, air removed. A valve is opened to allow workroom air to fill the flask. Analysis in laboratory, or with suitable field instruments. – Wash bottle, carboy, or other rigid-walled container. Flush container with workroom air to obtain a sample. Flush the bottle with 10 - 15 times the bottle volume. Water filled bottle is alternative. Methods of Sampling – Plastic bags, made of Tedlar, polyester, polyvinylidine chloride, other plastics. Useful sizes 5 - 15 L. Bags must be tested for leaks before use; polymer selection will consider storage, permeability, and reaction with bag walls and memory effects. 2 Methods of Sampling • Continuous (Integrated) sampling – Absorbers: dissolving gas in a liquid. Methods of Sampling • Continuous (Integrated sampling) – Chemical reactions are often used to stabilize substance before it leaves the liquid. (reduce volatility, e.g.) 3 Methods of Sampling • Samplers: gas washing bottles (impingers), fritted bubblers, spiral and helical absorbers, and glass-bead columns. – Methanol, Butanol in water; – Esters in alcohol examples of use for simple gas bubble (midget impinger). – Reactive samplers also use the midget impinger • TDI hydrolyzed to toluene diamine; • ammonia neutralized by sulfuric acid. • Cold traps use acetone in dry ice. Methods of Sampling • Solid Adsorbents (gas onto a solid) – Activated charcoal • can be efficiently desorbed with carbon disulfide. Optimal for nonpolar solvents. • Method • Breakthrough 4 Methods of Sampling – Silica gel • Polar contaminants: amines, some inorganics – Other sorbants include • synthetic polymers like XAD and Tenax. • Consistent in quality but more expensive. • Useful for low concentrations and unusual chemicals. Calculations • Calculations: to find concentration: m1 - mblank ( impinger ) SE × V + − C = m1 m2 mblank ( sorbent tube ) (DE × V) C= Ccorr ⎛ ⎞ ⎜ ⎟ ⎛ 760 ⎞⎜ T ⎟ = C⎜ ⎟ ⎝ P ⎠⎜ 298 ⎟ ⎜⎜ ⎟⎟ ⎝ ⎠ 5 Diffusive Samplers • Depend on flow of pollutant across a quiescent layer of air, or a membrane. Synonymous with passive dosimeter. Uses no pump to draw air across adsorbent. • Diffusion depends on well-established rules from physical chemistry, known as Fick's law. Two equations are used to predict solvent uptake Diffusive Samplers D( C a - C o ) L M C -C = (D)( a o ) At L D ( A) Mass = t (C a − C o ) L F= • F is flux units mg/cm2/sec • L is length if diffusion path, cm • D is diffusion coefficient, cm2/sec 6 Diffusive Samplers • Equations allow prediction of how much mass will be collected by the sampler; sample rate and efficiency are dictated by design of the device. Diffusive Samplers • Factors affecting performance: Independent of pressure, proportional to T½ . Humidity may reduce efficiency of charcoal samplers. Transients (peak exposures) do not affect performance, so long as sampling time is more than several minutes. Face velocity not too low or too high. 7 Diffusive Samplers • Calculation m1 + m 2 - mblank C= DExV Real Time Monitoring • Continuous monitors measure and report instantaneous observations of concentration. Supplemented by a means of recording data, a plot of air concentration vs. time can be generated. 8 Real Time Monitoring • Technologic developments – Digital meters – Data logging – Miniaturization – Multipoint monitoring Stationary Monitoring Systems • Uses – Warning or alarm systems – Monitor operation of controls – Identify problem areas – Generate a record of concentration – Define exposure problems 9 Real Time Monitoring • Description – Multipoint monitor vs. single point – Sensor(s) – Response time Advantages, Disadvantages • Real time data at several locations • Capable of warning of leaks before personnel are injured • Provide history of exposure data • Expensive • Complicated • Area monitor (not personal) 10 Personal Monitoring Systems • Personal dosimeters: data logging, computer interface, instantaneous response • Personal alarm monitors: intended to warn if air concentrations get too high. Advantages, Disadvantages • • • • • Portable Easy to use, stable and accurate Can be specific to vapors of concern Can monitor rapidly fluctuating concentrations Can provide detailed exposure profile for an individual worker • Limited number of chemicals can be monitored this way. • Increased maintenance (over pump/filter) 11 Direct-reading Instruments Characteristics • Specific or nonspecific: advantages and disadvantages to each, depends on the use of instrument Direct-reading Instrument Characteristics • Terms, accessories – – – – – – – – – Remote probes Data storage, transfer Alarm (variable settings) Ease of operation (some devices are complex) Response time (lag time) Saturation Sensor (sensor life) Probe Active/passive collection 12 Direct-reading Instruments: Characteristics – Hazardous atmospheres: instrument should be rated as intrinsically safe, if flammable air concentrations may be encountered. RF shielding may be needed. Direct-reading instruments • Calibration: conduct before each use, preferably with same contaminant as being monitored, else a reliable standard. • Use prepared standards, or generate your own. • Calibrate flow of pump, if it is included. • Calibration of aerosol monitors is more complex; may require factory calibration (periodic) 13 Recording Data • Data loggers allow collection of digitized information. • Data logger may be contained in monitor, or be a separate unit. • Transfer to a PC via dedicated cable and software. Recording Data • Dedicated printers: printers intended for use with specific pieces of equipment. • Allows a simple method of generating hard copy, user needs little knowledge of how to connect devices together. 14 Principles of Detection • Electrical Methods: Chemical and/or physical properties change electrical parameters in a gas or liquid. Amount of change is proportional to the concentration of the contaminant. Electrochemical cell 15 Principles of Detection • Conductivity: nonspecific method; electrolytes in aqueous solution change solution's conductivity. • Change is proportional to all ions present. Most useful when one contaminant predominates. • Temperature regulation is required. • Contaminants: H2S, SO2, NH3. – Some devices can detect Cl2, CO2 Principles of Detection • Potentiometry (measure potential difference): • Gases react with chemicals in solution to change the pH of the solution. • pH change is sensed electrically (ion flow.) • Choice of reagents can improve specificity. • Contaminants: Carbon monoxide, oxygen, carbon dioxide, many others. 16 Principles of Detection • Voltammetry: polarized electrodes. • Analyte moves to an electrode, gets oxidized, and resultant current is measured. Principles of Detection • Coulometry: Maintain a current in a cell; chemicals react in solution. • Contaminants: oxygen, ozone, H2S, nitrogen oxides, sulfur dioxide, HCN. 17 Principles of Detection • Ionization: Generate ions in a chamber, measure the number of ions collected on an electrode. • Method is nonspecific, in that any chemical species ionized will be measured. • Two types: – flame ionization detector (FID) – photo ionization detector (PID). • Contaminants: organic solvents, in a number of ranges (ppm to % LEL). Principles of Detection - FID 18 Principles of Detection - PID Principles of Detection • Thermal methods: use thermal properties of a gas to measure concentration. – Conductivity: Nonspecific method measuring thermal conductivity of a gas. – Combustion: Nonspecific method that measures the heat released during combustion. – Measure the change in electrical resistance across a heated filament. – Instruments may be refined using particular filaments or oxidation catalysts. Very common detection technique. 19 Principles of Detection • Spectroscopic and Photometric Methods – Use of electromagnetic energy (UV, IR, visible) to measure levels of contaminants. Most common method is absorption, but fluorescence, scattering, acoustic techniques are being developed. Principles of Detection • Methods depend on: – molecular absorption – emission – scatter 20 Principles of Detection • Infrared Photometry – Nondispersive Infrared (NDIR): – A band of IR light – Lasers, detectors or filters tune to specific wavelength(s) – CO2 is often measured with NDIR. Infrared detector - NDIR 21 Principles of Detection • Dispersive Infrared – employ a grating or prism to separate broadband light into component wavelengths. – Instruments can scan across IR region, to analyze for unknown gases. Infrared - IR 22 Principles of Detection Infrared • Chemical compounds absorb energy at characteristic wavelengths, depending on chemical structure. • IR absorption can be used to identify pure chemical compounds, or for air analysis. Principles of Detection • Ultraviolet photometers: – Absorption of UV radiation at particular wavelengths. • Mercury absorbs UV at 254 nm. Reduction of UV energy is a measure of mercury concentration. 23 Principles of Detection • Chemi-electromagnetic methods (chemical reaction followed by a measurement of electromagnetic radiation) – Colorimetry: Gas is sampled in a liquid or solid matrix, and color change takes place. – Choice of reactants can make monitor specific to vapor of concern. – Analysis involves selection of a choice of sensing cell and wavelengths to measure. – SO2 NOx NH3 , Cl2 , TDI, formaldehyde, cyanide, others. Principles of Detection • Chemiluminescent – substances are induced to emit electromagnetic radiation – Ozone reacts with Rhodamine B (a dye), and light at 585 nm is emitted. This emission can be detected by a photomultiplier tube, and is proportional to the mass of ozone in the detector. 24 Principles of Detection • Ozone reacts with ethylene and nitrogen oxide; • Each reaction results in specific light emission that can be measured proportionately to the mass of ozone or nitrogen oxide in the system. Principles of Detection • Colorimetric indicators – Development of detector tubes (SKC CD) • Colorimetric indicators may use liquid reagents, chemically treated papers or solid reagents. • Some simple laboratory methods have been packaged for field use; simple instructions can allow field analysis of reactive chemicals (e.g.: TDI, chromates, nitrogen oxides) 25 Principles of Detection • Chemically treated papers may react with specific chemicals to give a single color change or a range of colors, indicating concentration in air. • Sampling by diffusion or with use of a pump. • Commercial instruments use a paper tape to indicate concentration. Principles of Detection • Detector tubes contain specific chemicals in a small tube; • reagents react with chemicals in the sampled air to provide a color change (most commonly length-of-stain indication) to define contaminant concentration. 26 Principles of Detection • Applications: qualitative, quantitative evaluation of workroom air; air pollution studies subject to detection limitation; explosive atmosphere evaluation. Principles of Detection • Because of limitations and sources of error, qualified persons should make interpretations of results; despite simplicity, unskilled users may derive misleading results. 27

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